6
67 REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014 Abstract A mathematical model of the organic matter (chemical oxygen demand - COD) removal from synthetic oil-water emulsions by the electrocoagulation process was de- veloped to evaluate the COD abatement. The model comprises the three fundaments of electrocoagulation: electrochemistry, coagulation and flotation. By comparing the experimental and calculated values of COD, it was found that the model was able to adequately predict the concentrations of organic matter (COD) present in the emul- sions and satisfactorily describe the electrocoagulation process. Keywords: electrocoagulation, oil-water emulsions, organic matter (COD), mathemat- ical model. Resumo Um modelo matemático da remoção de matéria orgânica (demanda química de oxigênio - DQO) de emulsões sintéticas água-óleo pelo processo de eletrocoagulação foi desenvolvido para avaliar a redução da DQO. O modelo compreende os três fun- damentos da eletrocoagulação: coagulação, eletroquímica e flotação. Ao comparar os valores experimentais e calculados de DQO, verificou-se que o modelo foi capaz de predizer a concentração de matéria orgânica (DQO) presente nas emulsões e descrever satisfatoriamente o processo de eletrocoagulação. Palavras-chave: eletrocoagulação, emulsões óleo-água, matéria orgânica (DQO), mod- elo matemático. Rodolfo Maia Rangel D.Sc, Pontificia Universidade Católica do Rio de Janeiro Departamento de Engenharia de Materiais [email protected] Roberto José de Carvalho PhD, Pontif[icia Universidade Católica do Rio de Janeiro Departamento de Engenharia de Materiais [email protected] Maurício Leonardo Torem D.Sc. Pontificia Universidade Católica do Rio de Janeiro Departamento de Engenharia de Materiais [email protected] Organic matter removal from oil-water emulsions by electrocoagulation. 2 - Mathematical model Remoção de matéria orgânica de emulsões óleo-água por eletrocoagulação. 2 - Modelo matemático Metallurgy and materials Metalurgia e materiais

Metallurgy and materials - SciELO · lation: electrochemistry (represented by Faraday's law to predict the amount of aluminum cations generated at the an-ode as a function of time),

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67

Rodolfo Maia Rangel ed al.

REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014

Abstract

A mathematical model of the organic matter (chemical oxygen demand - COD) removal from synthetic oil-water emulsions by the electrocoagulation process was de-veloped to evaluate the COD abatement. The model comprises the three fundaments of electrocoagulation: electrochemistry, coagulation and flotation. By comparing the experimental and calculated values of COD, it was found that the model was able to adequately predict the concentrations of organic matter (COD) present in the emul-sions and satisfactorily describe the electrocoagulation process.

Keywords: electrocoagulation, oil-water emulsions, organic matter (COD), mathemat-ical model.

Resumo

Um modelo matemático da remoção de matéria orgânica (demanda química de oxigênio - DQO) de emulsões sintéticas água-óleo pelo processo de eletrocoagulação foi desenvolvido para avaliar a redução da DQO. O modelo compreende os três fun-damentos da eletrocoagulação: coagulação, eletroquímica e flotação. Ao comparar os valores experimentais e calculados de DQO, verificou-se que o modelo foi capaz de predizer a concentração de matéria orgânica (DQO) presente nas emulsões e descrever satisfatoriamente o processo de eletrocoagulação.

Palavras-chave: eletrocoagulação, emulsões óleo-água, matéria orgânica (DQO), mod-elo matemático.

Rodolfo Maia RangelD.Sc, Pontificia Universidade Católica do Rio de JaneiroDepartamento de Engenharia de Materiais [email protected]

Roberto José de CarvalhoPhD, Pontif[icia Universidade Católica do Rio de JaneiroDepartamento de Engenharia de [email protected]

Maurício Leonardo ToremD.Sc. Pontificia Universidade Católica do Rio de JaneiroDepartamento de Engenharia de [email protected]

Organic matter removal from oil-water emulsions by electrocoagulation. 2 - Mathematical model

Remoção de matéria orgânica de emulsões óleo-água por eletrocoagulação. 2 - Modelo matemático

Metallurgy and materialsMetalurgia e materiais

68

Organic matter removal from oil-water emulsions by electrocoagulation. 2 - Mathematical model

REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014

Oil-water emulsions are widely used in metal industries in processes such as roll-ing, forging and shaping. These emulsions have oil contents in the range 0.1 - 30 kg.m-3, depending on the specific application, are toxic and must be treated so that recycling of water is possible.

Several electrochemical methods have been studied over the years for the separa-tion of oil-water emulsions (Yang, 2007; Cañizares et al., 2008, Ibrahim et al., 2001,

Kramer et al., 1979). Electroflotation was one of the first processes developed in which oil is removed from emulsions previously destabilized by chemical additives. More recent efforts have been focused on the application of electrochemical techniques to destabilize ("break") the emulsion and separate the destabilized oil without the addition of chemical reagents. The key pro-cess involved in most of these techniques is electrocoagulation. Cañizares et al. (2008)

observed that the gas bubbles generated in electrocoagulation (oxygen at the anode and hydrogen at the cathode) promote the coalescence (electrofloculation) and the separation of coalesced droplets, which may be carried to the top of the emulsion and then collected and removed.

In this work, a mathematical model to predict the organic matter removal (drop of COD) from synthetic oil-water emulsions by electrocoagulation was developed.

1. Introduction

2. Materials and Methods

The oil-water emulsions and the experi- mental apparatus and procedure were described in part 1 of this work.

3. Results

The experimental results indicated that the oil-water emulsions presented good stability for initial pH values above 5, with average values of zeta potential around -75 mV. For initial pH below 5 the stability of the emulsions decreased as the average values of zeta potential were

approximately -40 mV. The values of con-ductivity were close to -0.6 S.m-1, except for experiments performed with NaCl elec-trolyte concentration of 1.0 kg.m-3. These values are suitable for the implementation of electrocoagulation. Regarding the kinet-ics, the higher the applied current density,

the faster was the removal of organic matter from the emulsion. Due to the fact that the current density is related to rate of production of Al3+ species, higher current densities led to shorter periods of latency and hence to lower total times to obtain high removals (over 95%).

4. Mathematical Model

The mathematical model involved the three fundamentals of electrocoagu-lation: electrochemistry (represented by Faraday's law to predict the amount of aluminum cations generated at the an-ode as a function of time), coagulation (represented by the chemical equilibrium between the organic matter and the Al3+ species) and flotation (represented by electroflotation during the inertia stage and flotation of the complexes during the

reactive stage).The curves of COD abatement

versus time exhibit three stages: a period of inertia in which the species Al3+ accu-mulated in the circuit and contributed to the reduction of the Zeta potential of the dispersed matter surface; a reactive stage where there was an increase in the COD removal probably due to low values of Zeta potential and possible agglomera-tion of the dispersion of Al3+ complexes;

a threshold for which additional addi-tion of Al3+ species did not allow further treatment.

The current density had a major effect on the COD removal rate, with higher values of current density resulting in shorter periods of inertia and hence in lower total times for the electrocoagula-tion process. It is well known that the effect of current density is associated with the rate of Al3+ species production.

The mathematical model took into account the following simplifying assumptions:i) Existence of a minimum concentration of aluminum, CAl,min, necessary to start the electrocoagulation process, and a corresponding minimum time for the oc-currence of such concentration, tmin. The minimum concentration of aluminum and the minimum time are related by Faraday's

law, i.e., CAl,min= (ηM I tmin)/(z F V), where M is the atomic mass of aluminum, I is the applied current, z is the number of electrons involved in the electrode reac-tion, is the Faraday's constant and V is the volume. Thus, it is considered that the amount of aluminum (Al3+) that is

produced in the cell is η times the value predicted by Faraday's law, although in re-ality the oxidation of aluminum occurs in two ways: electrochemical oxidation and chemical reaction at the anode (when the cathodes are not aluminum but an inert material such as stainless steel).

The minimum concentration of aluminum was expressed by the cor- relation:

where pHo is the initial pH of the emul-sion, COo is the initial oil concentration and A, B and C are constants determined by the experimental data.(ii) For aluminum concentrations lower than CAl,min and thus for times lower than tmin, the COD decrease does not

occur, which is characterized by a hori-zontal plateau in the curves. However, if there is an excess of surfactant it was assumed that only the COD related to the surfactant was reduced by electroflo-tation of that compound. Given that in the inertia stage the curves of COD

abatement resemble straight lines with non-zero slopes, a zero-order kinetics was assumed for the electroflotation, i.e.: COD= CODo- k t, where CODo is the initial COD and k is the rate cons-tant which depends on the experimen-tal variables.

CAl,min=A+B pHo+ C COo (1)

In the inertia stage the COD follows the correlation:

69

Rodolfo Maia Rangel ed al.

REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014

COD= CODo-(A+ B pHo+ C j+D COo+ E CE+ F δ ) t (2)

where j is the current density, CE is the electrolyte concentration, δ is the distance between electrodes, t is time and A, B, C, D, E and F are constants determined by the experimental data.

The statistical analysis of the data revealed that the contribution of the vari-ables δ and COo to equation (2) is negligible.

(iii) The organic matter contained in the emulsion was expressed in the model in terms of the amount of COD by the function Q(t). It was considered that the quantity of organic matter that cannot be removed by electrocoagulation is negligible. Hence the stabilization stage is characterized by very low values of COD

(less than 0.05 kg/m3). This assumption implies that all organic matter can be treated by electrocoagulation after addi-tion of coagulant and that at time zero, CODo = Q(0) = Q0.(iv) The electrocoagulation occurs by com-plexation of organic matter, Q, by Al3+ spe-cies through the “chemical equilibrium”:

Q+n Al=X (3)

where n is an overall coefficient (mg O2/mg Al3+) and X is the complex formed, which will be subsequently removed by flotation. Due to the unity of n the above equation

cannot be regarded as a real chemical process, but simply as a phenomenological description of the complexation of organic matter by aluminum species. Such descrip-

tion is adequate since the kinetic analysis revealed that the reaction rate depends on the concentrations of organic matter and aluminum (Rangel, 2008).

An overall “equilibrium” constant, K, was defined by:

K = [X]/[Q] [Al] (4)

where [Al] is the concentration of free aluminum species and [X] the con-centration of aluminum in a complex form.

The coefficient n was not in-cluded in the expression for the equi-librium constant, since reaction (3) cannot be deemed as an elementary

process at equilibrium.For times greater than the mini-

mum time, t > tmin, a mass balance on dissolved aluminum gives:

CAl= CAl,min+ [Al]+ 1/n [X] (5)

Substituting [Al] obtained by equation (4) in equation (5) the concentration of complex X is given by:

[X]= (n K [Q] (CAl- CAl,min ))/(n+K [Q] )

(v) The complex formed by organic matter and the Al3+ species was carried to the surface of the cell by hydrogen micro-bubbles generated on the stainless steel

cathodes. The mechanism of organic matter removal by sedimentation will be completely disregarded in view of the fairly high values of current density used in the

experiments. The flotation of the com-plexes to the surface followed a first order kinetics since this kinetics best represented the electrocoagulation data.

(6)

- d[X]/dt= K' [X] (7)

where K' is the rate constant for the complex flotation.

Integration of equation (7) from tmin and the corresponding concentration of the complex X, [X]min, not necessarily equal to 0 gives:

Equation (8) provides a mathematical expression for the variation of the organic matter concentration with time as a func-tion of the complexation "equilibrium" constant, K, the flotation rate constant, K', the minimum time for the onset of the reactive stage, tmin, the minimum aluminum concentration necessary for initiating the

electrocoagulation process, CAl,min, and the initial concentration of the complex, [X]min.

The methodology used for adjusting the model to the experimental results is described below.

It was not possible at first to identify the exact time (tmin) where the change from the inertia to the reactive stage took place,

i.e., the instant in which the COD drop was no longer linear in time and begun to follow equation (8). The time interval for which this change (inflection) has happened was then determined for each experiment. After establishing this time interval, the fitting of the model regarding the inertia stage was performed by equation (2) with:

(8)

k= A+ B pHo+ C j+D COo+ E CE+ F δ (9)

The rate constant k was determined using the numerical package Microsoft® Solver, which uses the least squares method to fit the experimental data. The

constants A, B, C, D, E and F were deter-mined using a multiple linear regression of the experimental variables. Therefore, COD values related to the inertia stage

were obtained and compared with those experimentally measured.

For the reactive stage, it was essen-tial to evaluate the minimum time, tmin,

70

Organic matter removal from oil-water emulsions by electrocoagulation. 2 - Mathematical model

REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014

5. Model Results

Equat ion (10) g ives the cor-re lat ion be t ween the rate con-

s tant , k , and the exper imenta l variables during the inertia stage.

The correlat ion coef f ic ient was 0.831.

k= 14.917- 5.479 pHo+ 16.847 j+9.530 COo+ 2.499 CE- 0.920 δ (10)

As expected, the rate constant increased with increasing current density, oil and electrolyte concen-tration, and decreased with increas-

ing initial pH and distance between electrodes.

The “equilibrium” constant, K, presented the following depen-

dence on the initial pH (correlation coefficient 0.9995) for the pH range 4-12. The contribution of the other variables was insignificant.

K=0.0941 pHo-5.967 (11)

According to equation (11) the com-plexation reaction becomes increasingly difficult as the initial pH of the emulsion increases. This finding is consistent with the Eh-pH diagrams in aqueous medium.

During the reactive stage, and espe-cially within its first few minutes, the ratio between the concentration of aluminum in a complex form and the concentration of free aluminum species is greater than 1. This means that during the electroco-agulation process the dissolved aluminum is primarily in the form of a complex with the organic matter. In addition, to begin the flotation of the complex, it is necessary to reach a minimum concentration of the complex, [X]min, which must obviously be less than the instantaneous concentration calculated from equation (6).

Correlations between the model parameters K', [X]min, n and CAl,min and the experimental variables were obtained. Given that most of the experiments was conducted with I = 2.0 A, δ = 0.01 m, COo = 3.0 kg.m-3 and CE = 3.0 kg.m-3, the pH should be the variable presenting the greatest impact on the model parameters since it varied in the 4-12 range.

The rate constant for the complexes flotation, K', was within the range -10-2 and -10-4 min-1. The negative sign is due to the fact that [X] needs to be greater than [X]min to occur the flotation of the complexes, as stated above. In another words, the negative sign of K' signifies that the rate of formation of the complexes is higher than the rate of their removal

from the solution by flotation, which also seems to be quite reasonable. It was also found that the dependency of K' with pH could be expressed through a sixth degree polynomial with a correlation coefficient of 0.9418.

The minimum concentration of complex required for the onset of flota-tion, [X]min, presented values betweeen 10-4 and 10-6 kg.m-3 and was, for all experiments, always lower than [X] cal-culated by equation (6). [X]min was also pH dependent, the dependency being ex-pressed by a third degree polynomial with a correlation coefficient of 0.9850. Gener-ally, [X]min decreased with increasing pH. As [X] also decreased with increasing pH, the reaction given by equation (3) is favored at lower pHs, as expected.

The overall coefficient, n, showed values in the range 10-4 a 10-2 mg O2/mg Al3+ except for experiments with pH 4.1, 10.8 and 12.1 for which the values were -5.53x1012, 2.24x107 and 2.86x107 mg O2/mg Al3+, respectively. These exceptions indicate that at acid pHs complexation oc-curs without the need for aluminum (very high and negative values of n) whereas at pHs (above 10.0) complexation would be very difficult requiring large amounts of coagulant. This result is consistent with the literature and confirms that the model is adequately describing the physical behavior of electrocoagulation. Usually the overall coefficient increased with in-creasing pH implying that the higher the pH, the greater the amount of coagulant

necessary to electrocoagulation. The overall coefficient was correlated to the pH by a third degree polynomial with a correlation coefficient of 0.9957.

The minimum concentration of aluminum for the onset of the reactive stage, CAl,min, displayed values of about 0.02 kg.m-3 (pH 4.1), 0.03 kg.m-3 (pH 7.2), 0.06 kg.m-3 (pH 8.0), from 0.09 to 1.00 kg.m-3 (pH between 8.5 and 9.5) and 1.10 kg.m-3 (pH between 10 and 12). Therefore, the higher the pH, the higher the CAl,min, which reflects a greater ease for the occurrence of complexation in slightly acid and neutral media and greater dif-ficulty in strongly alkaline media. The minimum concentration was found to be effectively dependent on pH, being ex-pressed by a sixth order polynomial with a correlation coefficient of 0.9524. Both the time required for the onset of the reac-tive stage and the duration of this stage decreased with increasing current density without influencing the concentration of aluminum required for the initiation of complexation with the organic matter. Accordingly, the minimum concentration should not be dependent on the current density.

To illustrate the application of the model five experiments involving different initial oil concentrations, current and ini-tial pH were selected and are summarized in Table 1. The surfactant concentration was 1.0 kg.m-3, the electrolyte concen-tration was 3.0 kg.m-3 and the distance between electrodes was 0.01 m.

and the minimum aluminum concentra-tion, CAl,min. For this the numerical package Solver was again utilized. The value of tmin that provided the best fit of the experimental data with equation (8) within the predetermined time interval

was determined.After finding out the inflection

point (tmin, CAl,min) the parameters K, K', [X]min and n that best matched the experimental data were assessed by the least squares method (Solver). These pa-

rameters were correlated to experimental variables studied.

Finally, the same procedure was repeated for the inertia stage and for the whole model, i.e., considering the two stages in sequence.

71

Rodolfo Maia Rangel ed al.

REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014

Table 1Selected experiments to illustrate the application of the model.

Figure 1Comparison between measured and cal-culated COD (Q) for experiment 1.

Figures 1-5 present the results of the comparison between the experimental values of COD and those calculated by

the model for the selected experiments. It is evident that the model adequately predicted the concentrations of organic

matter (COD) present in the emulsions. Similar results also occurred for all the other experiments.

Figure 2Comparison between measured and cal-culated COD (Q) for experiment 2.

Figure 3Comparison between measured and cal-culated COD (Q) for experiment 3.

72

Organic matter removal from oil-water emulsions by electrocoagulation. 2 - Mathematical model

REM: R. Esc. Minas, Ouro Preto, 67(1), 67-72, jan. mar. | 2014

Figure 4Comparison between measured and cal-

culated COD (Q) for experiment 4.

Figure 5Comparison between measured and cal-

culated COD (Q) for experiment 5.

6. Conclusions

The synthetic oil-water emulsions exhibited good stability for initial pH values above 5. The stability decreased for pHs lower than 5. The higher the value of current density, the faster is the removal of organic matter from the solution, allowing

shorter latency stages and therefore lower total times to attain high removals (over 95%). This result was ascribed to the fact that the current is related to the rate of production of Al3+ species.

The comparison between the experi-

mental values of COD and those calculated by the mathematical model substantiates its capacity to properly predict the concentra-tions of organic matter (COD) present in synthetic oil-water emulsions and satisfacto-rily describe the electrocoagulation process.

Acknowledgments

The authors acknowledge CNPq, Faperj and Capes for supporting this work and for providing a scholarship to Rodolfo Maia Rangel.

References

CAÑIZARES, P., MARTINEZ, F., JIMÉNEZ, C., SÁEZ, C., Rodrigo, M. A. Co-agulation and electrocoagulation of oil-in-water emulsions. Journal of Hazardous Materials, v. 151, p. 44-51, 2008.

IBRAHIM, M. Y., MOSTAFA, S. R., FAHMY, M. F. M., HAFEZ, A. I. Utilization of electroflotation in remediation of oily wastewater. Separation Science and Tech-nology, v. 36, n. 16, p. 3749-3762, 2001.

KRAMER, G. R., BUYERS, A., BROWNLEE, B. Electrolytic treatment for oily wa-stewater. In: PURDUE INDUSTRIAL WASTE CONFERENCE, 34, Lafayette, IN ,1979.p. 673.

RANGEL, R. M. Modelamento da eletrocoagulação aplicada ao tratamento de águas oleosas provenientes das indústrias extrativas. Departamento (Tese de Doutorado) de Engenharia de Materiais. Pontifícia Universidade Católica do Rio de Janeiro. Rio de Janeiro, 2008.

YANG, C-L. Electrochemical coagulation for oily water demulsification. Separation and Purification Technology, v. 54, p. 388-395, 2007.

Artigo recebido em 7 de junho de 2011. Aprovado em 23 de janeiro de 2014.